OHI: Species subgoal

1 Summary

Spatial data from IUCN and Aquamaps is combined with extinction risk information from IUCN to generate regional scores for the Species subgoal. A region’s status is based upon an area-weighted average of species health across each global reporting region.

From Halpern et al (2012):

The target for the Species sub-goal is to have all species at a risk status of Least Concern. We scaled the lower end of the biodiversity goal to be 0 when 75% species are extinct, a level comparable to the five documented mass extinctions and would constitute a catastrophic loss of biodiversity. The Status of assessed species was calculated as the area- and threat status-weighted average of the number of threatened species within each 0.5 degree grid cell.

Mean risk status per cell:

\[\bar{R}_{cell} = \frac{\displaystyle\sum_{species}(Risk)}{n_{spp}}\]

Mean risk status per region:

\[\bar{R}_{SPP} = \frac{\displaystyle\sum_{cells}(\bar{R}_{cell} * A_{cell} * pA_{cell-rgn})}{A_{rgn}}\]

Species goal model

\[X_{SPP} = \frac{((1 - \bar{R}_{SPP}) - 0.25)}{(1 - 0.25)} * 100%\]

where:

• \(X_{SPP}\) is Species goal status
• \(\bar{R}_{cell}\) is mean extinction risk for one cell
• \(\bar{R}_{SPP}\) is area-weighted mean extinction risk for a region
• \(A_{cell}\) is cell area
• \(pA_{cell-rgn}\) is percent of cell area included in region
• Risk is scaled value for species extinction risk category, based on:
  • ‘LC’ = 0.0, ‘NT’ = 0.2, ‘VU’ = 0.4, ‘EN’ = 0.6, ‘CR’ = 0.8, ‘EX’ = 1.0
• SPP trend is calculated in a similar area-weighted mean, but population trend values are assigned according to:
  • ‘Decreasing’ = -0.5, ‘Stable’ = 0.0, ‘Increasing’ = +0.5

2 Updates from previous assessment

Changes since 2015 SPP subgoal for global OHI:

• The 2016 assessment now includes bird species, based upon BirdLife International data. “Marine” bird species include any bird species with overlap of marine cells. (?) Prior assessments did not include this data.
• Previous assessments counted overlapping species as any species with a binomial included in both data sets (AquaMaps and IUCN/BirdLife). Synonyms were matched and typos were fixed manually where possible. This assessment takes advantage of the taxize package to identify and match synonyms for better match rate.
• Previous assessments used an AquaMaps threshold of 40% to determine whether a species counted as “present” within a cell. Based on the IUCN/AquaMaps manuscript, we are now using a 0% threshold for AquaMaps as it more closely resembles the “limits of distribution” criterion used for IUCN inclusion.
• Previous assessments ignored subpopulations for SPP; with IUCN’s newest data, a subpopulation field identifies distinct subpopulations (and IUCN risk codes) for a number of species (mostly mammals, but a handful of others as well). This allows us to incorporate subpopulation scores in the global assessment.
  • From http://www.iucnredlist.org/details/3897/0 (Loggerhead sea turtle):
    • Rationale: The global population of the Loggerhead Turtle (Caretta caretta) comprises 10 subpopulations (see Figure 2 in the Supplementary Material) that vary widely in population size, geographic range, and population trends, and are the appropriate units for assessment of global conservation status for this species (Wallace et al. 2010, 2011). As such, assessments have been completed for each of the 10 subpopulations, in addition to the combined global population assessment required by the IUCN (see Table 1 in the Supplementary Material). At the global level, both geographic distribution and population size are much larger than required to qualify for a threatened category. The available long-term series of nest counts (used as an index of population abundance) show an important decrease in the past (47%). Therefore, the Loggerhead Turtle is considered as Vulnerable under current IUCN Red List Criteria (criterion A2b). The previous listing, published in 1996, was Endangered under criterion A1bd (Marine Turtle Specialist Group 1996).
    • Results indicate that the Loggerhead Turtle, as a single taxonomic entity, will not go extinct globally in the next generation according to any Red List criteria. However, the global listing is not an appropriate representation of the conservation status of the biologically relevant subpopulations that make up the global Loggerhead Turtle population. Subpopulation assessments demonstrated wide variation not only in status of individual subpopulations (as indicated by IUCN Red List Categories), but also in the criteria under which the individual subpopulations qualified for a threatened category (see Table 1 in the Supplementary Material). For these reasons, the subpopulation-level assessments for the Loggerhead Turtle should be given priority in evaluating the true global conservation status of this species. This conclusion follows the precedent for other long-lived, widely distributed species, including the Leatherback Turtle (Wallace et al. 2013).

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3 Data Sources

IUCN:

• Reference:
  • IUCN 2015. The IUCN Red List of Threatened Species. Version 2015-4. http://www.iucnredlist.org.
    • Shapefiles available from: http://www.iucnredlist.org/technical-documents/spatial-data
    • Downloaded: 21 December 2015.
  • BirdLife International and NatureServe (2015) Bird species distribution maps of the world. BirdLife International, Cambridge, UK and NatureServe, Arlington, USA.
    • Zipped shapefile available from: http://www.biodiversityinfo.org/spcdownload/r5h8a1/ - username and password via BirdLife International.
      
    • Downloaded: 14 December 2015.
• Description: Shapefiles containing polygons of assessed species ranges; each shapefile represents all assessed species within a comprehensively-assessed (i.e. >90% assessed) taxonomic group.
• Native data resolution: NA
• Time range: NA
• Format: Shapefile

AquaMaps:

• Reference:
  • Kaschner, K., J. Rius-Barile, K. Kesner-Reyes, C.Garilao, S.O. Kullander, T. Rees and R. Froese (2013). AquaMaps: Predicted range maps for aquatic species. World wide web electronic publication, www.aquamaps.org, Version 08/2015.
    • Downloaded: August 2015.
• Description: .sql files containing information to recreate rasters of cell attributes and cell-by-cell probability of occurrence for 22889 marine species.
• Native data resolution: 0.5° latitude and longitude
  
• Time range: NA
• Format: SQL database files converted into .csv

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4 Methods

4.1 Extract AquaMaps data from .sql files

AquaMaps data for the 2016 assessment was provided as .sql files, as in previous years, that can be used to generate an SQL database. Each line in the .sql is a command to populate the SQL database.

• Original files extracted from aquamaps_2015_full_dataset_ohi.zip:
  • hcaf_ohi.sql
  • speciesoccursum_ohi.sql
  • hcaf_species_native_ohi.sql
• Processed files saved to git-annex:
  • hcaf_truncated.csv
  • speciesoccursum.csv
  • hcaf_sp_native_trunc.csv

To extract data, we instead scan each line for CREATE TABLE and INSERT INTO commands to create and save dataframes. Note that the am_extract_2015.R script discards much of the data from these .sqls that is not used within the OHI Species Goal processing (thus “truncated”). This speeds up read time and processing time and avoids parsing issues with some of the rows/columns. Note also that the hcaf_species_native_ohi.sql file does not originally contain LOICZID information; this is added in the extract script, since LOICZID as a cell identifier is faster and less memory intensive than CsquareCode (integer vs character string).

Half-degree cell info from hcaf_truncated.csv (first few rows)

csquarecode	loiczid	nlimit	slimit	wlimit	elimit	centerlat	centerlong	cellarea	oceanarea
5207:363:1	167254	-26.0	-26.5	-73.5	-73.0	-26.25	-73.25	2772.29	2772.29
5207:363:2	167253	-26.0	-26.5	-74.0	-73.5	-26.25	-73.75	2772.29	2772.29
5207:363:3	167974	-26.5	-27.0	-73.5	-73.0	-26.75	-73.25	2760.25	2760.25
5207:363:4	167973	-26.5	-27.0	-74.0	-73.5	-26.75	-73.75	2760.25	2760.25
5207:360:1	167260	-26.0	-26.5	-70.5	-70.0	-26.25	-70.25	2772.29	0.00

Species info from speciesoccursum.csv (first few rows)

speciesid	reviewed	speccode	genus	species	fbname	occurcells	kingdom	phylum	class	order	family	iucn_id	iucn_code	iucn_version
Fis-156671	null	62612	Abalistes	filamentosus	null	12	Animalia	Chordata	Actinopterygii	Tetraodontiformes	Balistidae	null	N.E.	2015-2
Fis-53544	1	9	Abalistes	stellaris	Starry triggerfish	198	Animalia	Chordata	Actinopterygii	Tetraodontiformes	Balistidae	null	N.E.	2015-2
Fis-142700	1	58334	Abalistes	stellatus	null	235	Animalia	Chordata	Actinopterygii	Tetraodontiformes	Balistidae	null	N.E.	2015-2
Fis-27725	1	10232	Ablabys	taenianotus	Cockatoo waspfish	59	Animalia	Chordata	Actinopterygii	Scorpaeniformes	Tetrarogidae	null	N.E.	2015-2
Fis-22975	1	972	Ablennes	hians	Flat needlefish	397	Animalia	Chordata	Actinopterygii	Beloniformes	Belonidae	null	N.E.	2015-2

Species-to-cell lookup from hcaf_sp_native_trunc.csv (first few rows)

speciesid	probability	loiczid
Fis-29358	1.00	129241
Fis-139729	0.97	129241
Fis-23185	0.81	129241
Fis-29263	1.00	129241
Fis-29290	1.00	129241

4.2 Ingest IUCN species list

To identify appropriate IUCN species for the analysis, we identified all IUCN Red List species whose habitat included “marine” designation. The ingest_iucn.R script scrapes this data directly from the IUCN Red List website.

• Starting point: Access Red List API at http://api.iucnredlist.org/index/all.csv. This provides a list of all Red List species, including unique IUCN code, taxonomic nomenclature, and Red List extinction risk.
• For all identified species, we access species-specific info at http://api.iucnredlist.org/details/X/0 where X is the unique IUCN species ID; this page is saved to a cache directory on git-annex as a .htm file. At the same time, we scrape the “habitats” field from the saved page using XML tags.
• All species with “marine” habitat are then scraped to find details on population trend and subpopulation ID numbers.
• After some cleaning of scientific names (accents, spaces, html tags, etc) the file is saved to git-annex for later use.

Processed files, saved to git-annex/globalprep/spp_ico/v201x/int: * spp_iucn_all.csv - full list of IUCN species pulled from web, some cleaning. * spp_iucn_habitats.csv - list of IUCN species (by iucn_sid) and corresponding habitat. * spp_iucn_marine.csv - prepped list: cleaned marine list with subpops and trends.

IUCN marine species list and info from spp_iucn_marine.csv (first few rows)

sciname	class	order	family	genus	species	authority	iucn_sid	modified_year	category	criteria	habitat	popn_trend	subpop_sid	parent_sid
Abantennarius analis	ACTINOPTERYGII	LOPHIIFORMES	ANTENNARIIDAE	Abantennarius	analis	(Schultz, 1957)	155277	2010	LC	NA	Marine	Unknown	NA	NA
Ablennes hians	ACTINOPTERYGII	BELONIFORMES	BELONIDAE	Ablennes	hians	(Valenciennes, 1846)	13486514	2015	LC	NA	Marine	Unknown	NA	NA
Ablennes pacificus	ACTINOPTERYGII	BELONIFORMES	BELONIDAE	Ablennes	pacificus	(Valenciennes, 1846)	13486514	2015	LC	NA	Marine	Unknown	NA	NA
Aboma etheostoma	ACTINOPTERYGII	PERCIFORMES	GOBIIDAE	Aboma	etheostoma	Jordan & Starks, 1895	183435	2010	DD	NA	Marine	Unknown	NA	NA
Aboma snyderi	ACTINOPTERYGII	PERCIFORMES	GOBIIDAE	Aboma	snyderi	(Temminck & Schlegel, 1845)	181137	2012	LC	NA	Marine	Unknown	NA	NA

4.3 Generate full species lookup table

Having processed AquaMaps and IUCN species raw data, we can now prepare a full combined list of all species to be included in the OHI SPP goal. The function create_spp_master_lookup() creates the full lookup table:

• Load AquaMaps species info from speciesoccursum.csv
  • Verify sciname field; the verify_scinames() function uses taxize::gnr_resolve() to compare AM scinames to accepted names from Encyclopedia of Life and NCBI databases - this helps resolve differences in naming conventions and species aliases.
• Load IUCN species info from spp_iucn_marine.csv
  • Verify sciname field as above.
• Join the two species lists by verified scientific names as the best common identifier.
• Create an extinction risk category field for each row, using IUCN category, or failing that the category listed in AquaMaps; failing that, assign NA.

At this point, the list is all AquaMaps species and all marine-identified IUCN species. Next, identify the source of spatial distribution data for each species, if available.

• From the downloaded IUCN shapefiles, determine which species have spatial data.
• Depending on preference and availability of spatial source (AquaMaps or IUCN), tag each row with a specific spatial_source (“am” or “iucn”).
• Follow a similar process for IUCN species included in the BirdLife International geodatabase (tag as “iucn-bli”).

Now having identified spatial source availability and preference for all species on the list:

• Clean out duplicated species
• Assign numeric values to population Red List category and population trend.
• Save result to git-annex/globalprep/spp_ico/v2016/int/spp_all_raw.csv
• Filter out subpop species rows (species with a non-NA parent_sid) that do not have a named subpopulation location (i.e. iucn_subpop field is NA, instead of the name of a subpopulation)
• Save final list to git-annex/globalprep/spp_ico/v2016/int/spp_all_cleaned.csv

Combined species list from spp_all_cleaned.csv (first few rows)

am_sid	am_cat	sciname	iucn_sid	pop_trend	pop_cat	spp_group	id_no	iucn_subpop	spatial_source	cat_score	trend_score
Fis-26169	LC	Apolemichthys trimaculatus	165835	Stable	LC	ANGELFISH	165835	NA	iucn	0	0
Fis-28014	LC	Apolemichthys xanthotis	165853	Stable	LC	ANGELFISH	165853	NA	iucn	0	0
Fis-28015	LC	Apolemichthys xanthurus	165844	Unknown	LC	ANGELFISH	165844	NA	iucn	0	NA
Fis-27342	LC	Centropyge acanthops	155083	Stable	LC	ANGELFISH	155083	NA	iucn	0	0
Fis-22168	LC	Centropyge argi	165837	Unknown	LC	ANGELFISH	165837	NA	iucn	0	NA

4.4 Spatialize species information using AquaMaps and IUCN spatial data

4.4.1 Extract IUCN polygons to half-degree cells

We extract IUCN polygon presence to the same half-degree cells as AquaMaps to simplify the analysis. * The spp_all species list includes a field spp_group that identifies which shapefile contains the spatial information for a given species. * for each species group, specific species are identified by comparing iucn_sid from dataframe to id_no within the shapefile. * Extract loiczid cell IDs for each species within each species group. Save a .csv file for that group, with fields: * sciname | iucn_sid | presence | subpop | LOICZID | prop_area * presence codes: 1 extant; 2 prob extant (discontinued); 3 Possibly Extant; 4 Possibly Extinct; 5 Extinct (post 1500); 6 Presence Uncertain * NOTE: this takes a long time - multiple hours for some of the shape files.
* by passing a filtered data frame to the function, you can focus the process only on new or updated shapefiles * reload = FALSE allows the function to skip extraction on groups with files already present. Set to TRUE if you need to extract an updated shapefile (or change the shapefile name, or delete the previous extraction…)

4.4.2 Generate cell-by-cell summary of species

For each half-degree cell, tally up the number of species present and determine a mean species risk value and population trend value for the cell.

• At this point, the species-cell lists are filtered to species with valid extinction risk categories - i.e. not DD and not NA.
• Since this averaging is done for each data set separately, we also track the species count per cell used to determine both the risk and the trend (separately, since many species with a risk value have no trend information, i.e. NA). These counts are used to weight the values when the two are combined.
• Data-set specific idiosyncracies:
  • For AquaMaps, we apply a threshold to set the minimum probability of occurrence that determines species “presence.”
  • For IUCN, no threshold is needed; but the shapefiles include a “presence” attribute in which a value of 5 indicates a region in which a subpopulation has become extinct. We use this to manually reset local extinction risk and trend to EX and NA respectively.
  • Note that for IUCN, we determine the proportional area when extracting polygons; currently we just consider any presence to fill the cell (similar to assuming even a low AquaMaps probability to indicate presence within the entire cell).

AquaMaps cell summary (first few rows)

loiczid	mean_cat_score	mean_pop_trend_score	n_cat_species	n_trend_species	source
8205	0	NaN	1	0	aquamaps
8206	0	NaN	1	0	aquamaps
8207	0	NaN	1	0	aquamaps
8209	0	NaN	1	0	aquamaps
8210	0	NaN	1	0	aquamaps
8211	0	NaN	1	0	aquamaps

IUCN cell summary (first few rows)

loiczid	mean_cat_score	mean_pop_trend_score	n_cat_species	n_trend_species	source
1	0.4	-0.5	1	1	iucn
2	0.4	-0.5	1	1	iucn
3	0.4	-0.5	1	1	iucn
4	0.4	-0.5	1	1	iucn
5	0.4	-0.5	1	1	iucn
6	0.4	-0.5	1	1	iucn

4.5 Summarize status and trend by region

Finally we take the two cell-by-cell summaries and combine, using a species-count weighting to determine the mean category and trend per cell. Cells are aggregated to regions, to calculate an area-weighted regional mean category, trend, and status.

These are then saved to status and trend layer outputs for global (shown in table) as well as 3 nautical mile, Antarctic, and High Seas regions.

4.6 Determine species by region

The calc_rgn_spp() function takes in lookup tables of species by cell (for both IUCN and AM), a cell-to-region lookup, and a species info lookup. From this it generates a list of which species occur in which regions, including species information.

Species by region - first few rows

iucn_sid	am_sid	sciname	pop_cat	pop_trend	spatial_source	rgn_id	rgn_name	n_cells	presence	n_spp_rgn
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	210	Japan	194	NA	11503
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	20	South Korea	35	NA	5861
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	255	DISPUTED	145	NA	18267
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	209	China	151	NA	10906
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	14	Taiwan	67	NA	10938
NA	Fis-156671	Abalistes filamentosus	NA	NA	am	207	Vietnam	113	NA	10348

4.7 Comparing scenarios and data

The following plots compare the status scores generated for the 2015 assessment to those generated for 2016.

• The first compares the released scores for 2015 to the proposed scores for 2016. This changes both the datasets and the methodology between the two axes.
  • 2015 scores used data from 2014 (d2014) for both AquaMaps and IUCN, and scripts from the v2015 scenario.
  • 2016 scores use data from 2015 (d2015) for both AquaMaps and IUCN, and scripts from the v2016 scenario.
• The first compares regenerated scores for 2015 to the proposed scores for 2016. This keeps the methodology largely the same between the two axes (except as noted below), and compares the changes in data.
  • 2015 scores used data from 2014 (d2014) for both AquaMaps and IUCN.
  • 2016 scores use data from 2015 (d2015) for both AquaMaps and IUCN.
  • Both scores use scripts from the v2016 scenario. Methodology exceptions:
    • AquaMaps for d2014 is processed with a 40% threshold (as in v2015) while d2015 is processed with a 0% threshold.
    • IUCN species-cell lookup for d2014 was generated using v2015 scripts, which relied on the sciname field for joining. I’ve added a step to add iucn_sid values according to sciname, to allow the species-cell lookup to work with the v2016 scripts.

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5 Provenance

• Run ID: 6 (99eedd8); run tag: “standard run”
• Run elapsed time: 3007.575 seconds; run memory usage: NA MB
• System info: System: Linux, Release: 4.4.0-16-generic. Machine: x86_64. User: ohara.
• Session info
  • R version: R version 3.2.5 (2016-04-14), Platform: x86_64-pc-linux-gnu, Running under: Ubuntu 14.04.4 LTS.
  • Attached base packages: parallel, stats, graphics, grDevices, utils, datasets, methods, base
  • Other attached packages: plotly_3.4.13, ggplot2_2.1.0, XML_3.98-1.4, RCurl_1.95-4.8, bitops_1.0-6, stringr_1.0.0, tidyr_0.4.1, dplyr_0.4.3, readr_0.2.2, rgdal_1.1-8, sp_1.2-2, data.table_1.9.6, foreign_0.8-66

## pre-main prep time: 3 ms

Provenance summary for run 6 (99eedd8): standard run (Fri May 6 13:50:44 2016)

file_name	file_dir	filetype	uncomm_chgs	commit_hash
am_cells_spp_prob0.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
cellID_regions_gcs_aq.csv	Mazu:/git-annex/globalprep/spp_ico/rgns	input	TRUE	NA
cellID_regions_gcs_global.csv	Mazu:/git-annex/globalprep/spp_ico/rgns	input	TRUE	NA
cellID_regions_gcs_global.csv	Mazu:/git-annex/globalprep/spp_ico/rgns	input	TRUE	NA
cellID_regions_gcs_hs.csv	Mazu:/git-annex/globalprep/spp_ico/rgns	input	TRUE	NA
cellID_rgn_offshore3nm_gcs_global.csv	Mazu:/git-annex/globalprep/spp_ico/rgns	input	TRUE	NA
cell_spp_summary_by_loiczid.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
cell_spp_summary_by_loiczid.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
cell_spp_summary_by_loiczid.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
cell_spp_summary_by_loiczid_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
hcaf.csv	Mazu:/git-annex/globalprep/_raw_data/aquamaps/d2015/../d2014/tables	input	TRUE	NA
hcaf_sp_native_trunc.csv	Mazu:/git-annex/globalprep/_raw_data/aquamaps/d2015/csv	input	TRUE	NA
hcaf_truncated.csv	Mazu:/git-annex/globalprep/_raw_data/aquamaps/d2015/csv	input	TRUE	NA
iucn_cells_spp.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
iucn_cells_spp.csv	Mazu:/git-annex/globalprep/spp_ico/v2015/int	input	TRUE	NA
ohi_hcaf_species_native.csv	Mazu:/git-annex/globalprep/_raw_data/aquamaps/d2015/../d2014/tables	input	TRUE	NA
rgn_spp_gl.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	input	FALSE	b21fe29
rgn_summary_3nm.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	07ea4c3
rgn_summary_aq.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
rgn_summary_gl.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	07ea4c3
rgn_summary_gl_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	07ea4c3
rgn_summary_hs.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	07ea4c3
speciesoccursum.csv	Mazu:/git-annex/globalprep/_raw_data/aquamaps/d2015/csv	input	TRUE	NA
spp_all_cleaned.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
spp_all_cleaned.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
spp_all.csv	Mazu:/git-annex/globalprep/spp_ico/v2015/int	input	TRUE	NA
spp_iucn_all.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
spp_iucn_habitats.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
spp_iucn_marine.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
spp_status_global.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	input	FALSE	07ea4c3
spp_status_global.csv	~/github/ohiprep/globalprep/spp_ico/v2015/data	input	FALSE	aaa53b5
spp_status_global_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	input	FALSE	07ea4c3
spp_sum_am_cells.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	07ea4c3
spp_sum_am_cells_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
spp_sum_iucn_cells.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	b21fe29
spp_sum_iucn_cells_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/summary	input	FALSE	5f8aba9
spp_trend_global.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	input	FALSE	07ea4c3
spp_trend_global.csv	~/github/ohiprep/globalprep/spp_ico/v2015/data	input	FALSE	aaa53b5
spp_trend_global_d14v16.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	input	FALSE	07ea4c3
trend_and_subpops.csv	Mazu:/git-annex/globalprep/spp_ico/v2016/int	input	TRUE	NA
rgn_spp_3nm.csv	~/github/ohiprep/globalprep/spp_ico/v2016/output	output	FALSE	5f8aba9
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